The daunting prospect of complete nitrate removal at DOE sites, such as the ERSP Oak Ridge Field Research Center (FRC), provides strong incentive to explore bioremediation strategies that will allow for uranium bioreduction and long-term stabilization in the presence of nitrate. The cost and effort required for complete nitrate removal from the FRC and similar DOE-contaminated sites may prove to be unworkable. For example, field tests of uranium bioreduction at the FRC have shown that nitrate levels rebound quickly and completely after cessation of active biostimulation
We have now added ethanol intermittently for over 700 days. Ethanol has been added weekly with each ...
The objective of this NETL sponsored bench-scale study was to demonstrate the efficacy of enhanced a...
Groundwater near the S3 ponds at the US Department of Energy's Y-12 site in Oak Ridge, Tennessee, is...
The potential for stimulating microbial U(VI) reduction as an in situ bioremediation strategy for ur...
The overall objective of this research is to understand the mechanisms for maintenance of bio-reduce...
Uranium contaminations of the subsurface in the vicinity of nuclear materials processing sites pose ...
Although the biogeochemical processes underlying key bioremediation technologies are increasingly we...
Bioreduction of U in contaminated sediments is an attractive strategy because of its low cost, and b...
In aerobic aquifers typical of many Department of Energy (DOE) legacy waste sites, uranium is presen...
This report summarizes progress made from June 2003 to July 2004. During this period research focuse...
This research focuses on the conditions and rates under which uranium will be remobilized after it h...
Mechanisms of nitrate-dependent U(IV) were assessed by incubating biogenic U(IV) with nitrite or Fe(...
This project represented a joint effort between Oak Ridge National Laboratory (ORNL), the University...
Groundwaters at nuclear sites are often characterised by low pH and high nitrate concentrations (10-...
Uranium and nitrate are common groundwater pollutants near in situ leach uranium mines. However, we ...
We have now added ethanol intermittently for over 700 days. Ethanol has been added weekly with each ...
The objective of this NETL sponsored bench-scale study was to demonstrate the efficacy of enhanced a...
Groundwater near the S3 ponds at the US Department of Energy's Y-12 site in Oak Ridge, Tennessee, is...
The potential for stimulating microbial U(VI) reduction as an in situ bioremediation strategy for ur...
The overall objective of this research is to understand the mechanisms for maintenance of bio-reduce...
Uranium contaminations of the subsurface in the vicinity of nuclear materials processing sites pose ...
Although the biogeochemical processes underlying key bioremediation technologies are increasingly we...
Bioreduction of U in contaminated sediments is an attractive strategy because of its low cost, and b...
In aerobic aquifers typical of many Department of Energy (DOE) legacy waste sites, uranium is presen...
This report summarizes progress made from June 2003 to July 2004. During this period research focuse...
This research focuses on the conditions and rates under which uranium will be remobilized after it h...
Mechanisms of nitrate-dependent U(IV) were assessed by incubating biogenic U(IV) with nitrite or Fe(...
This project represented a joint effort between Oak Ridge National Laboratory (ORNL), the University...
Groundwaters at nuclear sites are often characterised by low pH and high nitrate concentrations (10-...
Uranium and nitrate are common groundwater pollutants near in situ leach uranium mines. However, we ...
We have now added ethanol intermittently for over 700 days. Ethanol has been added weekly with each ...
The objective of this NETL sponsored bench-scale study was to demonstrate the efficacy of enhanced a...
Groundwater near the S3 ponds at the US Department of Energy's Y-12 site in Oak Ridge, Tennessee, is...